Cyproconazole; Pesticide Tolerance, 27756-27761 [E8-10829]
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27756
Federal Register / Vol. 73, No. 94 / Wednesday, May 14, 2008 / Rules and Regulations
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
I
Authority: 21 U.S.C. 321(q), 346a and 371.
2. Section 180.474 is amended in
paragraph (a)(1) in the table by
alphabetically adding the commodities
Almond, hulls and Nut, tree, group 14
and by revising the following
commodities to read as follows:
I
§ 180.474 Tebuconazole; tolerances for
residues.
(a) *
*
*
Commodity
Parts per million
Almond, hulls ..................
*
*
*
*
6.0
*
Barley, grain ...................
Barley, hay ......................
Barley, straw ...................
*
*
*
*
0.15
7.0
3.5
*
Nut, tree, group 14 .........
*
*
*
*
0.05
*
Wheat,
Wheat,
Wheat,
Wheat,
*
forage .................
grain ...................
hay .....................
straw ...................
*
*
*
3.0
0.05
7.0
1.5
*
[FR Doc. E8–10506 Filed 5–13–08; 8:45 am]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2008–0149; [FRL–8362–9]
Cyproconazole; Pesticide Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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AGENCY:
SUMMARY: This regulation establishes
tolerances for the free and conjugated
residues of cyproconazole, a-(4chlorophenyl)-a-(1-cyclopropylethyl)1H-1,2,4-triazole-1-ethanol in or on
aspirated grain fractions; field corn,
forage, grain and stover; soybean, seed,
forage, hay and oil; wheat, forage, hay,
straw, grain, grain, milled by products;
fat of cattle, goat, horse and sheep; and
meat byproducts (except liver) of cattle,
goat, horse and sheep. Additionally, this
regulation establishes tolerances for
cyproconazole and its metabolite, d-(4chlorophenyl)-b,d-dihydroxy-g-methyl1H-1,2,4-triazole-1-hexenoic acid in or
on milk and for cyproconazole and its
metabolite, 2-(4-chlorophenyl)-3cyclopropyl-1-[1,2,4]triazol-1-yl-butane2,3-diol in or on liver of cattle, goat,
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hog, horse, and sheep. Syngenta Crop
Protection, Inc., requested this tolerance
under the Federal Food, Drug, and
Cosmetic Act (FFDCA), as amended by
the Food Quality Protection Act of 1996
(FQPA).
DATES: This regulation is effective May
14, 2008. Objections and requests for
hearings must be received on or before
July 14, 2008, and must be filed in
accordance with the instructions
provided in 40 CFR part 178 (see also
Unit I.C. of the SUPPLEMENTARY
INFORMATION).
EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2008–0149. To access the
electronic docket, go to https://
www.regulations.gov, select ‘‘Advanced
Search,’’ then ‘‘Docket Search.’’ Insert
the docket ID number where indicated
and select the ‘‘Submit’’ button. Follow
the instructions on the regulations.gov
website to view the docket index or
access available documents. All
documents in the docket are listed in
the docket index available in
regulations.gov. Although listed in the
index, some information is not publicly
available, e.g., Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
FOR FURTHER INFORMATION CONTACT:
Mary L. Waller, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 308–9354; e-mail address:
waller.mary@epa.gov.
ADDRESSES:
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
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not limited to those engaged in the
following activities:
• Crop production (NAICS code 111),
e.g., agricultural workers; greenhouse,
nursery, and floriculture workers;
farmers.
• Animal production (NAICS code
112), e.g., cattle ranchers and farmers,
dairy cattle farmers, livestock farmers.
• Food manufacturing (NAICS code
311), e.g., agricultural workers; farmers;
greenhouse, nursery, and floriculture
workers; ranchers; pesticide applicators.
• Pesticide manufacturing (NAICS
code 32532), e.g., agricultural workers;
commercial applicators; farmers;
greenhouse, nursery, and floriculture
workers; residential users.
This listing is not intended to be
exhaustive, but rather to provide a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
B. How Can I Access Electronic Copies
of this Document?
In addition to accessing an electronic
copy of this Federal Register document
through the electronic docket at https://
www.regulations.gov, you may access
this Federal Register document
electronically through the EPA Internet
under the ‘‘Federal Register’’ listings at
https://www.epa.gov/fedrgstr. You may
also access a frequently updated
electronic version of EPA’s tolerance
regulations at 40 CFR part 180 through
the Government Printing Office’s pilot
e-CFR site at https://www.gpoaccess.gov/
ecfr.
C. Can I File an Objection or Hearing
Request?
Under section 408(g) of FFDCA, any
person may file an objection to any
aspect of this regulation and may also
request a hearing on those objections.
You must file your objection or request
a hearing on this regulation in
accordance with the instructions
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2008–0149 in the subject line on
the first page of your submission. All
requests must be in writing, and must be
mailed or delivered to the Hearing Clerk
as required by 40 CFR part 178 on or
before July 14, 2008.
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In addition to filing an objection or
hearing request with the Hearing Clerk
as described in 40 CFR part 178, please
submit a copy of the filing that does not
contain any CBI for inclusion in the
public docket that is described in
ADDRESSES. Information not marked
confidential pursuant to 40 CFR part 2
may be disclosed publicly by EPA
without prior notice. Submit this copy,
identified by docket ID number EPA–
HQ–OPP–2008–0149, by one of the
following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Mail: Office of Pesticide Programs
(OPP) Regulatory Public Docket (7502P),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001.
• Delivery: OPP Regulatory Public
Docket (7502P), Environmental
Protection Agency, Rm. S–4400, One
Potomac Yard (South Bldg.), 2777 S.
Crystal Dr., Arlington, VA. Deliveries
are only accepted during the Docket’s
normal hours of operation (8:30 a.m. to
4 p.m., Monday through Friday,
excluding legal holidays). Special
arrangements should be made for
deliveries of boxed information. The
Docket Facility telephone number is
(703) 305–5805.
II. Petition for Tolerance
In the Federal Register of November
22, 2006 (71 FR 67575) (FRL–8089–9),
EPA issued a notice pursuant to section
408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide petition (PP 6F7072) by
Syngenta Crop Protection, Inc., P.O. Box
18300, Greensboro, NC 27419–8300.
The petition requested that 40 CFR
180.485 be amended by establishing
tolerances for residues of the fungicide
cyproconazole, in or on the following
commodities: Soybean, seed at 0.05
parts per million (ppm); soybean, forage
at 1.0 ppm; soybean, hay at 2.5 ppm;
corn, field, grain at 0.02 ppm; corn,
field, forage at 0.6 ppm; corn, field,
stover at 1.5 ppm; wheat, straw at 1.0
ppm; wheat, grain at 0.05 ppm; wheat,
forage at 1.0 ppm; wheat, hay at 1.5
ppm; aspirated grain fractions at 0.6
ppm; cattle, fat at 0.01 ppm; cattle, liver
at 0.3 ppm; cattle, meat at 0.01 ppm;
cattle, meat byproducts (except liver) at
0.01 ppm; milk at 0.01 ppm; goat, fat at
0.01 ppm; goat, liver at 0.3 ppm; goat,
meat at 0.01 ppm; goat, meat byproducts
(except liver) at 0.01 ppm; hog, fat at
0.01 ppm; hog, liver at 0.3 ppm; hog
meat at 0.01 ppm; hog, meat byproducts
(except liver) at 0.01 ppm; horse, liver
at 0.3 ppm; horse, meat at 0.01 ppm;
horse, meat byproducts (except liver) at
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0.01 ppm; sheep, fat at 0.01 ppm; sheep,
kidney at 0.3 ppm; sheep, meat at 0.01
ppm; and sheep, meat byproducts
(except liver) at 0.01 ppm. This notice
included a summary of the petition
prepared by Syngenta Crop Protection,
Inc., the registrant. Comments were
received on the notice of filing. EPA’s
response to these comments is
discussed in Unit IV.C.
Based upon review of the data
supporting the petition, EPA concluded
that the preferred chemical name for
cyproconazole is ‘‘a-(4-chlorophenyl)-a(1-cyclopropylethyl)-1H-1,2,4-triazole-1ethanol.’’ 40 CFR 180.485 is being
revised to use this terminology. Also,
EPA determined that the time-limited
tolerance established for soybean seed
under 40 CFR 180.485(b) can be deleted
given that a tolerance for soybean seed
without time limitation is being
established in section (a).
Additionally, EPA has determined
that, as a result of the tolerances sought
in this petition, a tolerance is needed for
the combined free and conjugated
residues of cyproconazole a-(4chlorophenyl)-a-(1-cyclopropylethyl)1H-1,2,4-triazole-1-ethanol and its
metabolite [d-(4-chlorophenyl)-b,ddihydroxy-g-methyl-1H-1,2,4-triazole-1hexenoic acid in or on the commodity:
Milk at 0.02 ppm and that tolerances are
needed for the combined free and
conjugated residues of cyproconazole
[a-(4-chlorophenyl)-a-(1cyclopropylethyl)-1H-1,2,4-triazole-1ethanol and its metabolite [2-(4chlorophenyl)-3-cyclopropyl-1[1,2,4]triazol-1-yl-butane-2,3-diol in or
on the commodities: Liver of cattle,
goat, horse, and sheep at 0.50 ppm and
hog liver at 0.01 ppm.
III. Aggregate Risk Assessment and
Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA
allows EPA to establish a tolerance (the
legal limit for a pesticide chemical
residue in or on a food) only if EPA
determines that the tolerance is ‘‘safe.’’
Section 408(b)(2)(A)(ii) of FFDCA
defines ‘‘safe’’ to mean that ‘‘there is a
reasonable certainty that no harm will
result from aggregate exposure to the
pesticide chemical residue, including
all anticipated dietary exposures and all
other exposures for which there is
reliable information.’’ This includes
exposure through drinking water and in
residential settings, but does not include
occupational exposure. Section
408(b)(2)(C) of FFDCA requires EPA to
give special consideration to exposure
of infants and children to the pesticide
chemical residue in establishing a
tolerance and to ‘‘ensure that there is a
reasonable certainty that no harm will
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result to infants and children from
aggregate exposure to the pesticide
chemical residue....’’ These provisions
were added to FFDCA by the Food
Quality Protection Act (FQPA) of 1996.
EPA performs a number of analyses to
determine the risks from aggregate
exposure to pesticide residues. For
further discussion of the regulatory
requirements of section 408 of FFDCA
and a complete description of the risk
assessment process, see https://
www.epa.gov/fedrgstr/EPA-PEST/1997/
November/Day–26/p30948.htm.
Consistent with FFDCA section
408(b)(2)(D), and the factors specified in
FFDCA section 408(b)(2)(D), EPA has
reviewed the available scientific data
and other relevant information in
support of this action. EPA has
sufficient data to assess the hazards of
and to make a determination on
aggregate exposure for the petitionedfor-tolerance. EPA’s assessment of
exposures and risks associated with
establishing the tolerance follows.
A. Toxicological Profile
EPA has evaluated the available
toxicity data and considered its validity,
completeness, and reliability as well as
the relationship of the results of the
studies to human risk. EPA has also
considered available information
concerning the variability of the
sensitivities of major identifiable
subgroups of consumers, including
infants and children.
Specific information on the studies
received and the nature of the adverse
effects caused by cyproconazole as well
as the no-observed-adverse-effect-level
(NOAEL) and the lowest-observedadverse-effect-level (LOAEL) from the
toxicity studies can be found in the
docket established by this action, which
is described under ADDRESSES, and is
identified as ‘‘Cyproconazole: HumanHealth Risk Assessment for Proposed
Uses’’ in that docket.
B. Toxicological Endpoints
For hazards that have a threshold
below which there is no appreciable
risk, the toxicological level of concern
(LOC) is derived from the NOAEL in the
toxicology study identified as
appropriate for use in risk assessment.
However, if a NOAEL cannot be
determined, the LOAEL is sometimes
used for risk assessment. Uncertainty/
safety factors (UFs) are used in
conjunction with the LOC to take into
account uncertainties inherent in the
extrapolation from laboratory animal
data to humans and in the variations in
sensitivity among members of the
human population as well as other
unknowns. Safety is assessed for acute
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and chronic risks by comparing
aggregate exposure to the pesticide to
the acute population adjusted dose
(aPAD) and chronic population adjusted
dose (cPAD). The aPAD and cPAD are
calculated by dividing the LOC by all
applicable UFs. Short-term,
intermediate-term, and long-term risks
are evaluated by comparing aggregate
exposure to the LOC to ensure that the
margin of exposure (MOE) called for by
the product of all applicable UFs is not
exceeded.
For non-threshold risks, the Agency
assumes that any amount of exposure
will lead to some degree of risk and
estimates risk in terms of the probability
of occurrence of additional adverse
cases. Generally, cancer risks are
considered non-threshold. For more
information on the general principles
EPA uses in risk characterization and a
complete description of the risk
assessment process, see https://
www.epa.gov/fedrgstr/EPA-PEST/1997/
November/Day–26/p30948.htm.
A summary of the toxicological
endpoints for cyproconazole used for
human risk assessment can be found at
https://www.regulations.gov in document
‘‘Cyproconazole Human Health Risk
Assessment for Proposed Uses on Corn,
Soybean and Wheat’’ in docket ID
number EPA–HQ–OPP–2008–0149.
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C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to cyproconazole, EPA
considered exposure under the
petitioned-for tolerances as well as all
existing cyproconazole tolerances in 40
CFR 180.485. EPA assessed dietary
exposures from cyproconazole in food
as follows:
i. Acute exposure. Quantitative acute
dietary exposure and risk assessments
are performed for a food-use pesticide,
if a toxicological study has indicated the
possibility of an effect of concern
occurring as a result of a 1–day or single
exposure.
In estimating acute dietary exposure,
EPA used food consumption
information from the U.S. Department of
Agriculture (USDA) 1994–1996 and
1998 Nationwide Continuing Surveys of
Food Intake by Individuals (CSFII). As
to residue levels in food, EPA assumed
all foods for which there are tolerances
were treated and contain tolerance-level
residues.
ii. Chronic exposure. In conducting
this chronic dietary exposure
assessment EPA used the food
consumption data from the USDA 1994–
1996, or 1998 CSFII. As to residue levels
in food, EPA assumed all foods for
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which there are tolerances were treated
and contain tolerance-level residues.
iii. Cancer. Cyproconazole has been
classified by the Agency as ‘‘Not Likely
to be Carcinogenic to Humans’’. The
decision was based on the weight of
evidence that supports a non-genotoxic
mitogenic mode of action for
cyproconazole. Therefore, a cancer
dietary exposure assessment was not
performed.
2. Dietary exposure from drinking
water. The Agency lacks sufficient
monitoring data to complete a
comprehensive dietary exposure
analysis and risk assessment for
cyproconazole in drinking water.
Because the Agency does not have
comprehensive monitoring data,
drinking water concentration estimates
are made by reliance on simulation or
modeling taking into account data on
the environmental fate characteristics of
cyproconazole. Further information
regarding EPA drinking water models
used in pesticide exposure assessment
can be found at https://www.epa.gov/
oppefed1/models/water/index.htm.
Based on the FQPA Index Reservoir
Screening Tool (FIRST) and Screening
Concentration in Ground Water (SCIGROW) models, the estimated
environmental concentrations (EECs) of
cyproconazole for acute exposures are
estimated to be 1.14 parts per billion
(ppb) for surface water and 0.05 ppb for
ground water. The EECs for chronic
exposures are estimated to be 0.11 ppb
for surface water and 0.05 ppb for
ground water.
3. From non-dietary exposure. The
term ‘‘residential exposure’’ is used in
this document to refer to nonoccupational, non-dietary exposure
(e.g., for lawn and garden pest control,
indoor pest control, termiticides, and
flea and tick control on pets).
Cyproconazole is not registered for
use on any sites that would result in
residential exposure.
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of FFDCA
requires that, when considering whether
to establish, modify, or revoke a
tolerance, the Agency consider
‘‘available information’’ concerning the
cumulative effects of a particular
pesticide’s residues and ‘‘other
substances that have a common
mechanism of toxicity.’’
Unlike other pesticides for which EPA
has followed a cumulative risk approach
based on a common mechanism of
toxicity, EPA has not made a common
mechanism of toxicity finding for
cyproconazole and any other substance.
Other than as discussed below for the
cyproconazole metabolite 1,2,4-triazole
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for the purposes of this tolerance action,
therefore, EPA has assumed that
cyproconazole does not have a common
mechanism of toxicity with other
substances. For information regarding
EPA’s efforts to determine which
chemicals have a common mechanism
of toxicity and to evaluate the
cumulative effects of such chemicals,
see the policy statements released by
EPA’s Office of Pesticide Programs
concerning common mechanism
determinations and procedures for
cumulating effects from substances
found to have a common mechanism on
EPA’s website at https://www.epa.gov/
pesticides/cumulative/.
Cyproconazole is a triazole-derived
pesticide. This class of compounds can
form the common metabolite 1,2,4triazole and two triazole conjugates
(triazole alanine and triazole acetic
acid). To support existing tolerances
and to establish new tolerances for
triazole-derivative pesticides, including
cyproconazole, EPA conducted a human
health risk assessment for exposure to
1,2,4-triazole, triazole alanine, and
triazole acetic acid resulting from the
use of all current and pending uses of
any triazole-derived fungicide. The risk
assessment is a highly conservative,
screening-level evaluation in terms of
hazards associated with common
metabolites (e.g., use of a maximum
combination of uncertainty factors) and
potential dietary and non-dietary
exposures (i.e., high end estimates of
both dietary and non-dietary exposures).
In addition, the Agency retained the
additional 10X FQPA safety factor for
the protection of infants and children.
The assessment includes evaluations of
risks for various subgroups, including
those comprised of infants and children.
The Agency’s complete risk assessment
is found in the propiconazole
reregistration docket at https://
www.regulations.gov (docket ID EPA–
HQ–OPP–2005–0497). An addendum to
the risk assessment, ‘‘Dietary Exposure
Assessments for the Common Triazole
Metabolites 1,2,4-triazole,
Triazolylalanine, Triazolylacetic Acid
and Triazolyl Pyruvic Acid; Updated to
Include New Uses of Fenbuconazole,
Ipconazole, Metconazole, Tebuconazole,
and Uniconazole’’ can be found at
https://www.regulations.gov in docket ID
EPA–HQ–OPP–2008–0149.
D. Safety Factor for Infants and
Children
1. In general. Section 408 of FFDCA
provides that EPA shall apply an
additional (‘‘10X’’) tenfold margin of
safety for infants and children in the
case of threshold effects to account for
prenatal and postnatal toxicity and the
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completeness of the database on toxicity
and exposure unless EPA determines
based on reliable data that a different
margin of safety will be safe for infants
and children. This additional margin of
safety is commonly referred to as the
FQPA safety factor. In applying this
provision, EPA either retains the default
value of 10X when reliable data do not
support the choice of a different factor,
or, if reliable data are available, EPA
uses a different additional FQPA safety
factor value based on the use of
traditional UFs and/or special FQPA
safety factors, as appropriate.
2. Prenatal and postnatal sensitivity.
There is no evidence of increased
susceptibility in the developmental
study in rats or in the 2–generation
reproduction study in rat. There is no
concern for the increased susceptibility
in the New Zealand white (NZW) rabbit
study since clear NOAELs/LOAELs
were established for maternal and
developmental toxicities and
malformations were observed at doses
higher than the dose that produced
marginal maternal toxicity. The concern
is low for the increased susceptibility in
the Chinchilla rabbit study since the
incidences of hydrocephaly were low,
there was no dose response, high
concentration of the vehicle (CMC)
used, and the hydrocephaly was not
seen at the same doses in the NZW
strain of rabbit. Therefore, there is no
residual uncertainty for prenatal and/or
postnatal toxicity.
3. Conclusion. EPA has determined
that reliable data show that it would be
safe for infants and children to reduce
the FQPA safety factor to 1X. That
decision is based on the following
findings:
i. The toxicity database for
cyproconazole is complete.
ii. There is no indication that
cyproconazole is a neurotoxic chemical
and there is no need for a
developmental neurotoxicity study or
additional UFs to account for
neurotoxicity.
iii. Although there is qualitative
evidence of increased susceptibility in
the prenatal developmental studies in
rats and rabbits, EPA did not identify
any residual uncertainties after
establishing toxicity endpoints and
selecting traditional UFs to be used in
the risk assessment of cyproconazole.
iv. There are no residual uncertainties
identified in the exposure databases.
The dietary food exposure assessments
were performed based on 100% crop
treated (CT) and tolerance-level
residues. Conservative ground water
and surface water modeling estimates
were used. There are no residential uses
of cyproconazole.
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E. Aggregate Risks and Determination of
Safety
Safety is assessed for acute and
chronic risks by comparing aggregate
exposure to the pesticide to the aPAD
and cPAD. The aPAD and cPAD are
calculated by dividing the LOC by all
applicable UFs. For linear cancer risks,
EPA calculates the probability of
additional cancer cases given aggregate
exposure. Short-term, intermediateterm, and long-term risks are evaluated
by comparing aggregate exposure to the
LOC to ensure that the MOE called for
by the product of all applicable UFs is
not exceeded.
1. Acute risk. Using the exposure
assumptions discussed in this unit for
acute exposure, the acute dietary
exposure from food and water to
cyproconazole will occupy 3% of the
aPAD for the population group (females
13–49 years old).
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that exposure to cyproconazole from
food and water will utilize 13% of the
cPAD for the population group (children
1 – 2 years old). There are no residential
uses for cyproconazole that result in
chronic residential exposure to
cyproconazole.
3. Short-term risk. Short-term
aggregate exposure takes into account
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
Cyproconazole is not registered for
use on any sites that would result in
residential exposure. Therefore, the
aggregate risk is the sum of the risk from
food and water.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account residential exposure
plus chronic exposure to food and water
(considered to be a background
exposure level).
Cyproconazole is not registered for
use on any sites that would result in
residential exposure. Therefore, the
aggregate risk is the sum of the risk from
food and water, which do not exceed
the Agency’s LOC.
5. Aggregate cancer risk for U.S.
population. Cancer risk is expected to
be negligible because EPA concluded
that cyproconazole is not likely to be a
human carcinogen.
6. Determination of safety. Based on
these risk assessments, EPA concludes
that there is a reasonable certainty that
no harm will result to the general
population or to infants and children
from aggregate exposure to
cyproconazole residues.
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IV. Other Considerations
A. Analytical Enforcement Methodology
Method AM–0842–0790–0 for
determining cyproconazole in plant
commodities is an improved version of
the current enforcement, which allows
for use of either Nitrogen-Phosphorous
Detection (NPD) or Mass-Selective
Detection (MSD). As this method is
superior to the current enforcement
method, it will be forwarded to FDA to
either replace or supplement the
existing tolerance enforcement method
for plant commodities. The liguid
chromotography with tandem mass
spectrometry (LC-MS/MS) method
(Syngenta Method RAM 499/01) for
determining cyproconazole in livestock
commodities has undergone a
successful Independent Laboratory
Validation (ILV) trial and
radiovalidation trial. Therefore, a copy
of the method will be forwarded to the
Analytical Chemistry Branch for
evaluation as an enforcement method.
The methods may be requested from:
Chief, Analytical Chemistry Branch,
Environmental Science Center, 701
Mapes Rd., Ft. Meade, MD 20755–5350;
telephone number: (410) 305–2905; email address: residuemethods@epa.gov.
As metabolites in liver and in milk
need to be included in the tolerance
expression, enforcement methods will
be required for these residues. Methods
have been sent to the Analytical
Chemistry Branch for evaluation.
B. International Residue Limits
There are no established or proposed
Canadian or Codex maximum residue
limits (MRLs) for cyproconazole on food
or feed crops. Mexico has established
tolerances for cyproconazole at 0.05
ppm in barley and wheat grain, which
is equivalent to the recommended U.S.
tolerance for wheat grain. Therefore,
there are generally no questions about
the compatibility of the proposed
tolerances with international tolerances.
However, EPA notes that Japan has
established numerous tolerances for
cyproconazole, including MRLs on
wheat (0.2 ppm), corn (0.1 ppm), and
soybeans (0.05 ppm).
C. Response to Comment
Comments were received on the
notice of filing. EPA has responded to
similar comments from the commenter
on previous occasions. Refer to Federal
Register cites: 70 FR 37686 (June 30,
2005); 70 FR 1354 (January 7, 2005); and
69 FR 63083 (October 29, 2004).
V. Conclusion
Therefore, the tolerance is established
for free and conjugated residues of
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cyproconazole, a-(4-chlorophenyl)-a-(1cyclopropylethyl)-1H-1,2,4-triazole-1ethanol in or on the following
commodities at the indicated tolerance
levels in parts per million.
Aspirated grain fractions . . . 2.5
Corn, field, forage, . . . 0.60
Corn, field, grain . . . 0.01
Corn, field, stover . . . 1.2
Fat of cattle, goat, horse and sheep. .
. 0.01
Meat byproducts (except liver) of
cattle, goat, horse and sheep . . .0.01
Soybean, seed . . . 0.05
Soybean, forage . . . 1.0
Soybean hay . . .3.0
Soybean, oil . . . 0.10
Wheat, forage . . . 0.80
Wheat, hay . . . 1.3
Wheat, straw . . . 0.90
Wheat, grain . . . 0.05
Wheat, grain, milled byproducts . . .
0.10
A tolerance is also established for the
combined free and conjugated residues
of cyproconazole [a-(4-chlorophenyl)-a(1-cyclopropylethyl)-1H-1,2,4-triazole-1ethanol] and its metabolite [d-(4chlorophenyl)-b,d-dihydroxy-g-methyl1H-1,2,4-triazole-1-hexenoic acid in or
on the following commodity:
Milk. . . 0.02
Also, tolerances are established for
the combined free and conjugated
residues of cyproconazole a-(4chlorophenyl)-a-(1-cyclopropylethyl)1H-1,2,4-triazole-1-ethanol and its
metabolite [2-(4-chlorophenyl)-3cyclopropyl-1-[1,2,4]triazol-1-yl-butane2,3-diol in or on the following
commodities:
Liver of cattle, goat, horse, and sheep
. . . 0.50
Hog liver . . . 0.01
rfrederick on PROD1PC67 with RULES
VI. Statutory and Executive Order
Reviews
This final rule establishes a tolerance
under section 408(d) of FFDCA in
response to a petition submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled Regulatory
Planning and Review (58 FR 51735,
October 4, 1993). Because this rule has
been exempted from review under
Executive Order 12866, this rule is not
subject to Executive Order 13211,
Actions Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001) or Executive Order 13045,
entitled Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997).
This final rule does not contain any
information collections subject to OMB
approval under the Paperwork
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14:57 May 13, 2008
Jkt 214001
Reduction Act (PRA), 44 U.S.C. 3501 et
seq., nor does it require any special
considerations under Executive Order
12898, entitled Federal Actions to
Address Environmental Justice in
Minority Populations and Low-Income
Populations (59 FR 7629, February 16,
1994).
Since tolerances and exemptions that
are established on the basis of a petition
under section 408(d) of FFDCA, such as
the tolerance in this final rule, do not
require the issuance of a proposed rule,
the requirements of the Regulatory
Flexibility Act (RFA) (5 U.S.C. 601 et
seq.) do not apply.
This final rule directly regulates
growers, food processors, food handlers,
and food retailers, not States or tribes,
nor does this action alter the
relationships or distribution of power
and responsibilities established by
Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such,
the Agency has determined that this
action will not have a substantial direct
effect on States or tribal governments,
on the relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
tribes. Thus, the Agency has determined
that Executive Order 13132, entitled
Federalism (64 FR 43255, August 10,
1999) and Executive Order 13175,
entitled Consultation and Coordination
with Indian Tribal Governments (65 FR
67249, November 6, 2000) do not apply
to this rule. In addition, This rule does
not impose any enforceable duty or
contain any unfunded mandate as
described under Title II of the Unfunded
Mandates Reform Act of 1995 (UMRA)
(Public Law 104–4).
This action does not involve any
technical standards that would require
Agency consideration of voluntary
consensus standards pursuant to section
12(d) of the National Technology
Transfer and Advancement Act of 1995
(NTTAA), Public Law 104–113, section
12(d) (15 U.S.C. 272 note).
VII. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report to each House of
the Congress and to the Comptroller
General of the United States. EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of this final rule in the
PO 00000
Frm 00040
Fmt 4700
Sfmt 4700
Federal Register. This final rule is not
a ‘‘major rule’’ as defined by 5 U.S.C.
804(2).
List of Subjects in 40 CFR Part 180
Environmental protection.
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: May 6, 2008.
Deborah McCall,
Acting Director, Registration Division, Office
of Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
I
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
I
Authority: 21 U.S.C. 321(q), 346a and 371.
2. Section 180.485 is amended by
revising paragraph (a) and removing the
text from paragraph (b) and reserving to
read as follows:
I
§ 180.485 Cyproconazole; tolerances for
residues.
(a) General. (1) Tolerances are
established for the free and conjugated
residues of the fungicide cyproconazole,
a-(4-chlorophenyl)-a-(1cyclopropylethyl)-1H-1,2,4-triazole-1ethanol, in or on the following food
commodities:
Commodity
Aspirated grain fractions
Cattle, fat ........................
Cattle, meat byproducts
(except liver) ...............
Coffee bean, green (Imported)1 .......................
Corn, field, forage ...........
Corn, field, grain .............
Corn, field, stover ...........
Goat, fat ..........................
Goat, meat byproducts
(except liver) ...............
Horse, fat ........................
Horse, meat byproducts
(except liver) ...............
Sheep, fat .......................
Sheep, meat byproducts
(except liver) ...............
Soybean, forage .............
Soybean, hay ..................
Soybean, oil ....................
Soybean, seed ................
Wheat, forage .................
Wheat, grain ...................
Wheat, grain, milled byproducts ......................
Wheat, hay .....................
Wheat, straw ...................
Parts per million
2.5
0.01
0.01
0.1
0.60
0.01
1.2
0.01
0.01
0.01
0.01
0.01
0.01
1.0
3.0
0.10
0.05
0.80
0.05
0.10
1.3
0.90
1There are no U.S. registrations as of February 15, 2008 for use on coffee bean.
(2) A tolerance is established for the
combined free and conjugated residues
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Federal Register / Vol. 73, No. 94 / Wednesday, May 14, 2008 / Rules and Regulations
of cyproconazole a-(4-chlorophenyl)-a(1-cyclopropylethyl)-1H-1,2,4-triazole-1ethanol] and its metabolite [d-(4chlorophenyl)-b,d-dihydroxy-g-methyl1H-1,2,4-triazole-1-hexenoic acid in or
on the following commodity:
Commodity
Parts per million
Milk .................................
0.02
(3) Tolerances are established for the
combined free and conjugated residues
of cyproconazole a-(4-chlorophenyl)-a(1-cyclopropylethyl)-1H-1,2,4-triazole-1ethanol and its metabolite 2-(4chlorophenyl)-3-cyclopropyl-1[1,2,4]triazol-1-yl-butane-2,3-diol in or
on the following commodities:
Commodity
Parts per million
Cattle, liver ......................
Goat, liver .......................
Hog, liver ........................
Horse, liver .....................
Sheep, liver .....................
0.50
0.50
0.01
0.50
0.50
(b) Section 18 emergency exemptions.
[Reserved]
*
*
*
*
*
[FR Doc. E8–10829 Filed 5–13–08; 8:45 am]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 268
[EPA–HQ–RCRA–2007–0936; FRL–8565–9]
Land Disposal Restrictions: SiteSpecific Treatment Variance for P- and
U-Listed Hazardous Mixed Wastes
Treated by Vacuum Thermal
Desorption at the Energy Solutions’
Facility in Clive, UT
Environmental Protection
Agency.
ACTION: Final rule.
rfrederick on PROD1PC67 with RULES
AGENCY:
SUMMARY: The Environmental Protection
Agency (EPA or the Agency) is
promulgating a final rule granting a sitespecific treatment variance to
EnergySolutions LLC (EnergySolutions)
in Clive, Utah for the treatment of
certain P- and U-listed hazardous waste
containing radioactive contamination
(‘‘mixed waste’’) using vacuum thermal
desorption (VTD). This variance is an
alternative treatment standard to
treatment by combustion (CMBST)
required for these wastes under EPA’s
rules in implementing the land disposal
restriction (LDR) provisions of the
Resource Conservation and Recovery
Act (RCRA). The Agency has
determined that combustion of the solid
VerDate Aug<31>2005
14:57 May 13, 2008
Jkt 214001
treatment residue generated from the
VTD unit is technically inappropriate
due to the effective performance of the
VTD unit. Thus, once the P- and Ulisted mixed waste are treated using the
VTD unit, the solid treatment residue
can be land disposed without further
treatment. This variance is conditioned
upon EnergySolutions complying with a
Waste Family Demonstration Testing
(WFDT) plan specifically addressing the
treatment of these P- and U-listed
wastes, which is to be implemented
through a RCRA Part B permit
modification for the VTD unit.
DATES: This final rule will be effective
June 13, 2008.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. EPA–HQ–RCRA–2007–0936. All
documents in the docket are listed on
the https://www.regulations.gov Web
site. Although listed in the index, some
information may not be publicly
available, because for example, it may
be Confidential Business Information
(CBI) or other information, the
disclosure of which is restricted by
statute. Certain material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
https://www.regulations.gov or in hard
copy at the RCRA Docket, EPA/DC, EPA
West, Room 3334, 1301 Constitution
Avenue, NW., Washington, DC. The
Docket Facility is open from 8:30 a.m.
to 4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the RCRA Docket is (202)
566–0270. A reasonable fee may be
charged for copying docket materials.
FOR FURTHER INFORMATION CONTACT: For
more information on this rulemaking,
contact Elaine Eby, Hazardous Waste
Minimization and Management
Division, Office of Solid Waste (MC
5302 P), U.S. Environmental Protection
Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460; telephone (703)
308–8449; fax (703) 308–8443; or
eby.elaine@epa.gov.
SUPPLEMENTARY INFORMATION:
A. Does This Action Apply to Me?
This action applies only to
EnergySolutions located in Clive, Utah.
B. Table of Contents
I. Summary of This Action
II. Background
III. Development of This Variance
A. EnergySolutions’ Petition
PO 00000
Frm 00041
Fmt 4700
Sfmt 4700
27761
B. Comments Received on Variance and
the Agency’s Response
C. What Type and How Much Mixed Waste
Are Subject to This Variance?
D. Description of the VTD Process
IV. EPA’s Reasons for Granting This Variance
V. Conditions of the Variance
VI. Statutory and Executive Orders
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act of 1995
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. Summary of This Action
EPA is promulgating, as proposed, a
site-specific treatment variance to
EnergySolutions in Clive, Utah for the
treatment of certain P- and U-listed
mixed waste using an alternative
treatment standard of VTD.1 The current
treatment standard for these wastes is
combustion (CMBST). See 40 CFR
268.40 and 268.42.
EnergySolutions’ VTD unit currently
operates pursuant to a Part B RCRA
permit issued by the State of Utah
which (among other things) authorizes
the treatment of mixed waste containing
both semi-volatile organic compounds
(SVOC) and volatile organic compounds
(VOC). In 2006, EnergySolutions
submitted a petition to EPA for a sitespecific treatment variance from the
LDR treatment standard of CMBST for
various P- and U-listed mixed waste.
The petitioner is seeking an alternative
treatment standard of VTD.
1 Mixed waste is defined as radioactive waste that
contains hazardous waste that either: (1) Is listed as
a hazardous waste in Subpart D of 40 CFR Part 261;
or (2) causes the waste to exhibit any of the
hazardous waste characteristics identified in
Subpart C of 40 CFR Part 261. Mixed waste is
regulated under multiple authorities: RCRA (for the
non-radioactive component), as implemented by
EPA or authorized States; and the Atomic Energy
Act (AEA) (for the source, special nuclear, or byproduct material component), as implemented by
the Nuclear Regulatory Commission (NRC), NRC
agreement States (for commercially-generated
mixed wastes), or the Department of Energy (DOE)
(for defense-related mixed waste generated by DOE
activities). The variance is limited to the RCRA
requirements for treatment of the hazardous waste
portion of the mixed waste and does not affect the
regulations under AEA authority.
E:\FR\FM\14MYR1.SGM
14MYR1
Agencies
[Federal Register Volume 73, Number 94 (Wednesday, May 14, 2008)]
[Rules and Regulations]
[Pages 27756-27761]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-10829]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2008-0149; [FRL-8362-9]
Cyproconazole; Pesticide Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes tolerances for the free and
conjugated residues of cyproconazole, [alpha]-(4-chlorophenyl)-[alpha]-
(1-cyclopropylethyl)-1H-1,2,4-triazole-1-ethanol in or on aspirated
grain fractions; field corn, forage, grain and stover; soybean, seed,
forage, hay and oil; wheat, forage, hay, straw, grain, grain, milled by
products; fat of cattle, goat, horse and sheep; and meat byproducts
(except liver) of cattle, goat, horse and sheep. Additionally, this
regulation establishes tolerances for cyproconazole and its metabolite,
[delta]-(4-chlorophenyl)-[beta],[delta]-dihydroxy-[gamma]-methyl-1H-
1,2,4-triazole-1-hexenoic acid in or on milk and for cyproconazole and
its metabolite, 2-(4-chlorophenyl)-3-cyclopropyl-1-[1,2,4]triazol-1-yl-
butane-2,3-diol in or on liver of cattle, goat, hog, horse, and sheep.
Syngenta Crop Protection, Inc., requested this tolerance under the
Federal Food, Drug, and Cosmetic Act (FFDCA), as amended by the Food
Quality Protection Act of 1996 (FQPA).
DATES: This regulation is effective May 14, 2008. Objections and
requests for hearings must be received on or before July 14, 2008, and
must be filed in accordance with the instructions provided in 40 CFR
part 178 (see also Unit I.C. of the SUPPLEMENTARY INFORMATION).
ADDRESSES: EPA has established a docket for this action under docket
identification (ID) number EPA-HQ-OPP-2008-0149. To access the
electronic docket, go to https://www.regulations.gov, select ``Advanced
Search,'' then ``Docket Search.'' Insert the docket ID number where
indicated and select the ``Submit'' button. Follow the instructions on
the regulations.gov website to view the docket index or access
available documents. All documents in the docket are listed in the
docket index available in regulations.gov. Although listed in the
index, some information is not publicly available, e.g., Confidential
Business Information (CBI) or other information whose disclosure is
restricted by statute. Certain other material, such as copyrighted
material, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available in the electronic docket at https://www.regulations.gov, or,
if only available in hard copy, at the OPP Regulatory Public Docket in
Rm. S-4400, One Potomac Yard (South Bldg.), 2777 S. Crystal Dr.,
Arlington, VA. The Docket Facility is open from 8:30 a.m. to 4 p.m.,
Monday through Friday, excluding legal holidays. The Docket Facility
telephone number is (703) 305-5805.
FOR FURTHER INFORMATION CONTACT: Mary L. Waller, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 308-9354; e-mail address: waller.mary@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be potentially affected by this action if you are an
agricultural producer, food manufacturer, or pesticide manufacturer.
Potentially affected entities may include, but are not limited to those
engaged in the following activities:
Crop production (NAICS code 111), e.g., agricultural
workers; greenhouse, nursery, and floriculture workers; farmers.
Animal production (NAICS code 112), e.g., cattle ranchers
and farmers, dairy cattle farmers, livestock farmers.
Food manufacturing (NAICS code 311), e.g., agricultural
workers; farmers; greenhouse, nursery, and floriculture workers;
ranchers; pesticide applicators.
Pesticide manufacturing (NAICS code 32532), e.g.,
agricultural workers; commercial applicators; farmers; greenhouse,
nursery, and floriculture workers; residential users.
This listing is not intended to be exhaustive, but rather to
provide a guide for readers regarding entities likely to be affected by
this action. Other types of entities not listed in this unit could also
be affected. The North American Industrial Classification System
(NAICS) codes have been provided to assist you and others in
determining whether this action might apply to certain entities. If you
have any questions regarding the applicability of this action to a
particular entity, consult the person listed under FOR FURTHER
INFORMATION CONTACT.
B. How Can I Access Electronic Copies of this Document?
In addition to accessing an electronic copy of this Federal
Register document through the electronic docket at https://
www.regulations.gov, you may access this Federal Register document
electronically through the EPA Internet under the ``Federal Register''
listings at https://www.epa.gov/fedrgstr. You may also access a
frequently updated electronic version of EPA's tolerance regulations at
40 CFR part 180 through the Government Printing Office's pilot e-CFR
site at https://www.gpoaccess.gov/ecfr.
C. Can I File an Objection or Hearing Request?
Under section 408(g) of FFDCA, any person may file an objection to
any aspect of this regulation and may also request a hearing on those
objections. You must file your objection or request a hearing on this
regulation in accordance with the instructions provided in 40 CFR part
178. To ensure proper receipt by EPA, you must identify docket ID
number EPA-HQ-OPP-2008-0149 in the subject line on the first page of
your submission. All requests must be in writing, and must be mailed or
delivered to the Hearing Clerk as required by 40 CFR part 178 on or
before July 14, 2008.
[[Page 27757]]
In addition to filing an objection or hearing request with the
Hearing Clerk as described in 40 CFR part 178, please submit a copy of
the filing that does not contain any CBI for inclusion in the public
docket that is described in ADDRESSES. Information not marked
confidential pursuant to 40 CFR part 2 may be disclosed publicly by EPA
without prior notice. Submit this copy, identified by docket ID number
EPA-HQ-OPP-2008-0149, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Mail: Office of Pesticide Programs (OPP) Regulatory Public
Docket (7502P), Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460-0001.
Delivery: OPP Regulatory Public Docket (7502P),
Environmental Protection Agency, Rm. S-4400, One Potomac Yard (South
Bldg.), 2777 S. Crystal Dr., Arlington, VA. Deliveries are only
accepted during the Docket's normal hours of operation (8:30 a.m. to 4
p.m., Monday through Friday, excluding legal holidays). Special
arrangements should be made for deliveries of boxed information. The
Docket Facility telephone number is (703) 305-5805.
II. Petition for Tolerance
In the Federal Register of November 22, 2006 (71 FR 67575) (FRL-
8089-9), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP
6F7072) by Syngenta Crop Protection, Inc., P.O. Box 18300, Greensboro,
NC 27419-8300. The petition requested that 40 CFR 180.485 be amended by
establishing tolerances for residues of the fungicide cyproconazole, in
or on the following commodities: Soybean, seed at 0.05 parts per
million (ppm); soybean, forage at 1.0 ppm; soybean, hay at 2.5 ppm;
corn, field, grain at 0.02 ppm; corn, field, forage at 0.6 ppm; corn,
field, stover at 1.5 ppm; wheat, straw at 1.0 ppm; wheat, grain at 0.05
ppm; wheat, forage at 1.0 ppm; wheat, hay at 1.5 ppm; aspirated grain
fractions at 0.6 ppm; cattle, fat at 0.01 ppm; cattle, liver at 0.3
ppm; cattle, meat at 0.01 ppm; cattle, meat byproducts (except liver)
at 0.01 ppm; milk at 0.01 ppm; goat, fat at 0.01 ppm; goat, liver at
0.3 ppm; goat, meat at 0.01 ppm; goat, meat byproducts (except liver)
at 0.01 ppm; hog, fat at 0.01 ppm; hog, liver at 0.3 ppm; hog meat at
0.01 ppm; hog, meat byproducts (except liver) at 0.01 ppm; horse, liver
at 0.3 ppm; horse, meat at 0.01 ppm; horse, meat byproducts (except
liver) at 0.01 ppm; sheep, fat at 0.01 ppm; sheep, kidney at 0.3 ppm;
sheep, meat at 0.01 ppm; and sheep, meat byproducts (except liver) at
0.01 ppm. This notice included a summary of the petition prepared by
Syngenta Crop Protection, Inc., the registrant. Comments were received
on the notice of filing. EPA's response to these comments is discussed
in Unit IV.C.
Based upon review of the data supporting the petition, EPA
concluded that the preferred chemical name for cyproconazole is
``[alpha]-(4-chlorophenyl)-[alpha]-(1-cyclopropylethyl)-1H-1,2,4-
triazole-1-ethanol.'' 40 CFR 180.485 is being revised to use this
terminology. Also, EPA determined that the time-limited tolerance
established for soybean seed under 40 CFR 180.485(b) can be deleted
given that a tolerance for soybean seed without time limitation is
being established in section (a).
Additionally, EPA has determined that, as a result of the
tolerances sought in this petition, a tolerance is needed for the
combined free and conjugated residues of cyproconazole [alpha]-(4-
chlorophenyl)-[alpha]-(1-cyclopropylethyl)-1H-1,2,4-triazole-1-ethanol
and its metabolite [[delta]-(4-chlorophenyl)-[beta],[delta]-dihydroxy-
[gamma]-methyl-1H-1,2,4-triazole-1-hexenoic acid in or on the
commodity: Milk at 0.02 ppm and that tolerances are needed for the
combined free and conjugated residues of cyproconazole [[alpha]-(4-
chlorophenyl)-[alpha]-(1-cyclopropylethyl)-1H-1,2,4-triazole-1-ethanol
and its metabolite [2-(4-chlorophenyl)-3-cyclopropyl-1-[1,2,4]triazol-
1-yl-butane-2,3-diol in or on the commodities: Liver of cattle, goat,
horse, and sheep at 0.50 ppm and hog liver at 0.01 ppm.
III. Aggregate Risk Assessment and Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a
tolerance (the legal limit for a pesticide chemical residue in or on a
food) only if EPA determines that the tolerance is ``safe.'' Section
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a
reasonable certainty that no harm will result from aggregate exposure
to the pesticide chemical residue, including all anticipated dietary
exposures and all other exposures for which there is reliable
information.'' This includes exposure through drinking water and in
residential settings, but does not include occupational exposure.
Section 408(b)(2)(C) of FFDCA requires EPA to give special
consideration to exposure of infants and children to the pesticide
chemical residue in establishing a tolerance and to ``ensure that there
is a reasonable certainty that no harm will result to infants and
children from aggregate exposure to the pesticide chemical
residue....'' These provisions were added to FFDCA by the Food Quality
Protection Act (FQPA) of 1996.
EPA performs a number of analyses to determine the risks from
aggregate exposure to pesticide residues. For further discussion of the
regulatory requirements of section 408 of FFDCA and a complete
description of the risk assessment process, see https://www.epa.gov/
fedrgstr/EPA-PEST/1997/November/Day-26/p30948.htm.
Consistent with FFDCA section 408(b)(2)(D), and the factors
specified in FFDCA section 408(b)(2)(D), EPA has reviewed the available
scientific data and other relevant information in support of this
action. EPA has sufficient data to assess the hazards of and to make a
determination on aggregate exposure for the petitioned-for-tolerance.
EPA's assessment of exposures and risks associated with establishing
the tolerance follows.
A. Toxicological Profile
EPA has evaluated the available toxicity data and considered its
validity, completeness, and reliability as well as the relationship of
the results of the studies to human risk. EPA has also considered
available information concerning the variability of the sensitivities
of major identifiable subgroups of consumers, including infants and
children.
Specific information on the studies received and the nature of the
adverse effects caused by cyproconazole as well as the no-observed-
adverse-effect-level (NOAEL) and the lowest-observed-adverse-effect-
level (LOAEL) from the toxicity studies can be found in the docket
established by this action, which is described under ADDRESSES, and is
identified as ``Cyproconazole: Human-Health Risk Assessment for
Proposed Uses'' in that docket.
B. Toxicological Endpoints
For hazards that have a threshold below which there is no
appreciable risk, the toxicological level of concern (LOC) is derived
from the NOAEL in the toxicology study identified as appropriate for
use in risk assessment. However, if a NOAEL cannot be determined, the
LOAEL is sometimes used for risk assessment. Uncertainty/safety factors
(UFs) are used in conjunction with the LOC to take into account
uncertainties inherent in the extrapolation from laboratory animal data
to humans and in the variations in sensitivity among members of the
human population as well as other unknowns. Safety is assessed for
acute
[[Page 27758]]
and chronic risks by comparing aggregate exposure to the pesticide to
the acute population adjusted dose (aPAD) and chronic population
adjusted dose (cPAD). The aPAD and cPAD are calculated by dividing the
LOC by all applicable UFs. Short-term, intermediate-term, and long-term
risks are evaluated by comparing aggregate exposure to the LOC to
ensure that the margin of exposure (MOE) called for by the product of
all applicable UFs is not exceeded.
For non-threshold risks, the Agency assumes that any amount of
exposure will lead to some degree of risk and estimates risk in terms
of the probability of occurrence of additional adverse cases.
Generally, cancer risks are considered non-threshold. For more
information on the general principles EPA uses in risk characterization
and a complete description of the risk assessment process, see https://
www.epa.gov/fedrgstr/EPA-PEST/1997/November/Day-26/p30948.htm.
A summary of the toxicological endpoints for cyproconazole used for
human risk assessment can be found at https://www.regulations.gov in
document ``Cyproconazole Human Health Risk Assessment for Proposed Uses
on Corn, Soybean and Wheat'' in docket ID number EPA-HQ-OPP-2008-0149.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to cyproconazole, EPA considered exposure under the
petitioned-for tolerances as well as all existing cyproconazole
tolerances in 40 CFR 180.485. EPA assessed dietary exposures from
cyproconazole in food as follows:
i. Acute exposure. Quantitative acute dietary exposure and risk
assessments are performed for a food-use pesticide, if a toxicological
study has indicated the possibility of an effect of concern occurring
as a result of a 1-day or single exposure.
In estimating acute dietary exposure, EPA used food consumption
information from the U.S. Department of Agriculture (USDA) 1994-1996
and 1998 Nationwide Continuing Surveys of Food Intake by Individuals
(CSFII). As to residue levels in food, EPA assumed all foods for which
there are tolerances were treated and contain tolerance-level residues.
ii. Chronic exposure. In conducting this chronic dietary exposure
assessment EPA used the food consumption data from the USDA 1994-1996,
or 1998 CSFII. As to residue levels in food, EPA assumed all foods for
which there are tolerances were treated and contain tolerance-level
residues.
iii. Cancer. Cyproconazole has been classified by the Agency as
``Not Likely to be Carcinogenic to Humans''. The decision was based on
the weight of evidence that supports a non-genotoxic mitogenic mode of
action for cyproconazole. Therefore, a cancer dietary exposure
assessment was not performed.
2. Dietary exposure from drinking water. The Agency lacks
sufficient monitoring data to complete a comprehensive dietary exposure
analysis and risk assessment for cyproconazole in drinking water.
Because the Agency does not have comprehensive monitoring data,
drinking water concentration estimates are made by reliance on
simulation or modeling taking into account data on the environmental
fate characteristics of cyproconazole. Further information regarding
EPA drinking water models used in pesticide exposure assessment can be
found at https://www.epa.gov/oppefed1/models/water/index.htm.
Based on the FQPA Index Reservoir Screening Tool (FIRST) and
Screening Concentration in Ground Water (SCI-GROW) models, the
estimated environmental concentrations (EECs) of cyproconazole for
acute exposures are estimated to be 1.14 parts per billion (ppb) for
surface water and 0.05 ppb for ground water. The EECs for chronic
exposures are estimated to be 0.11 ppb for surface water and 0.05 ppb
for ground water.
3. From non-dietary exposure. The term ``residential exposure'' is
used in this document to refer to non-occupational, non-dietary
exposure (e.g., for lawn and garden pest control, indoor pest control,
termiticides, and flea and tick control on pets).
Cyproconazole is not registered for use on any sites that would
result in residential exposure.
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when
considering whether to establish, modify, or revoke a tolerance, the
Agency consider ``available information'' concerning the cumulative
effects of a particular pesticide's residues and ``other substances
that have a common mechanism of toxicity.''
Unlike other pesticides for which EPA has followed a cumulative
risk approach based on a common mechanism of toxicity, EPA has not made
a common mechanism of toxicity finding for cyproconazole and any other
substance. Other than as discussed below for the cyproconazole
metabolite 1,2,4-triazole for the purposes of this tolerance action,
therefore, EPA has assumed that cyproconazole does not have a common
mechanism of toxicity with other substances. For information regarding
EPA's efforts to determine which chemicals have a common mechanism of
toxicity and to evaluate the cumulative effects of such chemicals, see
the policy statements released by EPA's Office of Pesticide Programs
concerning common mechanism determinations and procedures for
cumulating effects from substances found to have a common mechanism on
EPA's website at https://www.epa.gov/pesticides/cumulative/.
Cyproconazole is a triazole-derived pesticide. This class of
compounds can form the common metabolite 1,2,4-triazole and two
triazole conjugates (triazole alanine and triazole acetic acid). To
support existing tolerances and to establish new tolerances for
triazole-derivative pesticides, including cyproconazole, EPA conducted
a human health risk assessment for exposure to 1,2,4-triazole, triazole
alanine, and triazole acetic acid resulting from the use of all current
and pending uses of any triazole-derived fungicide. The risk assessment
is a highly conservative, screening-level evaluation in terms of
hazards associated with common metabolites (e.g., use of a maximum
combination of uncertainty factors) and potential dietary and non-
dietary exposures (i.e., high end estimates of both dietary and non-
dietary exposures). In addition, the Agency retained the additional 10X
FQPA safety factor for the protection of infants and children. The
assessment includes evaluations of risks for various subgroups,
including those comprised of infants and children. The Agency's
complete risk assessment is found in the propiconazole reregistration
docket at https://www.regulations.gov (docket ID EPA-HQ-OPP-2005-0497).
An addendum to the risk assessment, ``Dietary Exposure Assessments for
the Common Triazole Metabolites 1,2,4-triazole, Triazolylalanine,
Triazolylacetic Acid and Triazolyl Pyruvic Acid; Updated to Include New
Uses of Fenbuconazole, Ipconazole, Metconazole, Tebuconazole, and
Uniconazole'' can be found at https://www.regulations.gov in docket ID
EPA-HQ-OPP-2008-0149.
D. Safety Factor for Infants and Children
1. In general. Section 408 of FFDCA provides that EPA shall apply
an additional (``10X'') tenfold margin of safety for infants and
children in the case of threshold effects to account for prenatal and
postnatal toxicity and the
[[Page 27759]]
completeness of the database on toxicity and exposure unless EPA
determines based on reliable data that a different margin of safety
will be safe for infants and children. This additional margin of safety
is commonly referred to as the FQPA safety factor. In applying this
provision, EPA either retains the default value of 10X when reliable
data do not support the choice of a different factor, or, if reliable
data are available, EPA uses a different additional FQPA safety factor
value based on the use of traditional UFs and/or special FQPA safety
factors, as appropriate.
2. Prenatal and postnatal sensitivity. There is no evidence of
increased susceptibility in the developmental study in rats or in the
2-generation reproduction study in rat. There is no concern for the
increased susceptibility in the New Zealand white (NZW) rabbit study
since clear NOAELs/LOAELs were established for maternal and
developmental toxicities and malformations were observed at doses
higher than the dose that produced marginal maternal toxicity. The
concern is low for the increased susceptibility in the Chinchilla
rabbit study since the incidences of hydrocephaly were low, there was
no dose response, high concentration of the vehicle (CMC) used, and the
hydrocephaly was not seen at the same doses in the NZW strain of
rabbit. Therefore, there is no residual uncertainty for prenatal and/or
postnatal toxicity.
3. Conclusion. EPA has determined that reliable data show that it
would be safe for infants and children to reduce the FQPA safety factor
to 1X. That decision is based on the following findings:
i. The toxicity database for cyproconazole is complete.
ii. There is no indication that cyproconazole is a neurotoxic
chemical and there is no need for a developmental neurotoxicity study
or additional UFs to account for neurotoxicity.
iii. Although there is qualitative evidence of increased
susceptibility in the prenatal developmental studies in rats and
rabbits, EPA did not identify any residual uncertainties after
establishing toxicity endpoints and selecting traditional UFs to be
used in the risk assessment of cyproconazole.
iv. There are no residual uncertainties identified in the exposure
databases. The dietary food exposure assessments were performed based
on 100% crop treated (CT) and tolerance-level residues. Conservative
ground water and surface water modeling estimates were used. There are
no residential uses of cyproconazole.
E. Aggregate Risks and Determination of Safety
Safety is assessed for acute and chronic risks by comparing
aggregate exposure to the pesticide to the aPAD and cPAD. The aPAD and
cPAD are calculated by dividing the LOC by all applicable UFs. For
linear cancer risks, EPA calculates the probability of additional
cancer cases given aggregate exposure. Short-term, intermediate-term,
and long-term risks are evaluated by comparing aggregate exposure to
the LOC to ensure that the MOE called for by the product of all
applicable UFs is not exceeded.
1. Acute risk. Using the exposure assumptions discussed in this
unit for acute exposure, the acute dietary exposure from food and water
to cyproconazole will occupy 3% of the aPAD for the population group
(females 13-49 years old).
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that exposure to
cyproconazole from food and water will utilize 13% of the cPAD for the
population group (children 1 - 2 years old). There are no residential
uses for cyproconazole that result in chronic residential exposure to
cyproconazole.
3. Short-term risk. Short-term aggregate exposure takes into
account residential exposure plus chronic exposure to food and water
(considered to be a background exposure level).
Cyproconazole is not registered for use on any sites that would
result in residential exposure. Therefore, the aggregate risk is the
sum of the risk from food and water.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account residential exposure plus chronic exposure to food
and water (considered to be a background exposure level).
Cyproconazole is not registered for use on any sites that would
result in residential exposure. Therefore, the aggregate risk is the
sum of the risk from food and water, which do not exceed the Agency's
LOC.
5. Aggregate cancer risk for U.S. population. Cancer risk is
expected to be negligible because EPA concluded that cyproconazole is
not likely to be a human carcinogen.
6. Determination of safety. Based on these risk assessments, EPA
concludes that there is a reasonable certainty that no harm will result
to the general population or to infants and children from aggregate
exposure to cyproconazole residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Method AM-0842-0790-0 for determining cyproconazole in plant
commodities is an improved version of the current enforcement, which
allows for use of either Nitrogen-Phosphorous Detection (NPD) or Mass-
Selective Detection (MSD). As this method is superior to the current
enforcement method, it will be forwarded to FDA to either replace or
supplement the existing tolerance enforcement method for plant
commodities. The liguid chromotography with tandem mass spectrometry
(LC-MS/MS) method (Syngenta Method RAM 499/01) for determining
cyproconazole in livestock commodities has undergone a successful
Independent Laboratory Validation (ILV) trial and radiovalidation
trial. Therefore, a copy of the method will be forwarded to the
Analytical Chemistry Branch for evaluation as an enforcement method.
The methods may be requested from: Chief, Analytical Chemistry Branch,
Environmental Science Center, 701 Mapes Rd., Ft. Meade, MD 20755-5350;
telephone number: (410) 305-2905; e-mail address:
residuemethods@epa.gov.
As metabolites in liver and in milk need to be included in the
tolerance expression, enforcement methods will be required for these
residues. Methods have been sent to the Analytical Chemistry Branch for
evaluation.
B. International Residue Limits
There are no established or proposed Canadian or Codex maximum
residue limits (MRLs) for cyproconazole on food or feed crops. Mexico
has established tolerances for cyproconazole at 0.05 ppm in barley and
wheat grain, which is equivalent to the recommended U.S. tolerance for
wheat grain. Therefore, there are generally no questions about the
compatibility of the proposed tolerances with international tolerances.
However, EPA notes that Japan has established numerous tolerances for
cyproconazole, including MRLs on wheat (0.2 ppm), corn (0.1 ppm), and
soybeans (0.05 ppm).
C. Response to Comment
Comments were received on the notice of filing. EPA has responded
to similar comments from the commenter on previous occasions. Refer to
Federal Register cites: 70 FR 37686 (June 30, 2005); 70 FR 1354
(January 7, 2005); and 69 FR 63083 (October 29, 2004).
V. Conclusion
Therefore, the tolerance is established for free and conjugated
residues of
[[Page 27760]]
cyproconazole, [alpha]-(4-chlorophenyl)-[alpha]-(1-cyclopropylethyl)-
1H-1,2,4-triazole-1-ethanol in or on the following commodities at the
indicated tolerance levels in parts per million.
Aspirated grain fractions . . . 2.5
Corn, field, forage, . . . 0.60
Corn, field, grain . . . 0.01
Corn, field, stover . . . 1.2
Fat of cattle, goat, horse and sheep. . . 0.01
Meat byproducts (except liver) of cattle, goat, horse and sheep . .
.0.01
Soybean, seed . . . 0.05
Soybean, forage . . . 1.0
Soybean hay . . .3.0
Soybean, oil . . . 0.10
Wheat, forage . . . 0.80
Wheat, hay . . . 1.3
Wheat, straw . . . 0.90
Wheat, grain . . . 0.05
Wheat, grain, milled byproducts . . . 0.10
A tolerance is also established for the combined free and
conjugated residues of cyproconazole [[alpha]-(4-chlorophenyl)-[alpha]-
(1-cyclopropylethyl)-1H-1,2,4-triazole-1-ethanol] and its metabolite
[[delta]-(4-chlorophenyl)-[beta],[delta]-dihydroxy-[gamma]-methyl-1H-
1,2,4-triazole-1-hexenoic acid in or on the following commodity:
Milk. . . 0.02
Also, tolerances are established for the combined free and
conjugated residues of cyproconazole [alpha]-(4-chlorophenyl)-[alpha]-
(1-cyclopropylethyl)-1H-1,2,4-triazole-1-ethanol and its metabolite [2-
(4-chlorophenyl)-3-cyclopropyl-1-[1,2,4]triazol-1-yl-butane-2,3-diol in
or on the following commodities:
Liver of cattle, goat, horse, and sheep . . . 0.50
Hog liver . . . 0.01
VI. Statutory and Executive Order Reviews
This final rule establishes a tolerance under section 408(d) of
FFDCA in response to a petition submitted to the Agency. The Office of
Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993). Because this rule has been
exempted from review under Executive Order 12866, this rule is not
subject to Executive Order 13211, Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use (66 FR 28355,
May 22, 2001) or Executive Order 13045, entitled Protection of Children
from Environmental Health Risks and Safety Risks (62 FR 19885, April
23, 1997). This final rule does not contain any information collections
subject to OMB approval under the Paperwork Reduction Act (PRA), 44
U.S.C. 3501 et seq., nor does it require any special considerations
under Executive Order 12898, entitled Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations (59 FR 7629, February 16, 1994).
Since tolerances and exemptions that are established on the basis
of a petition under section 408(d) of FFDCA, such as the tolerance in
this final rule, do not require the issuance of a proposed rule, the
requirements of the Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et
seq.) do not apply.
This final rule directly regulates growers, food processors, food
handlers, and food retailers, not States or tribes, nor does this
action alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such, the Agency has determined that
this action will not have a substantial direct effect on States or
tribal governments, on the relationship between the national government
and the States or tribal governments, or on the distribution of power
and responsibilities among the various levels of government or between
the Federal Government and Indian tribes. Thus, the Agency has
determined that Executive Order 13132, entitled Federalism (64 FR
43255, August 10, 1999) and Executive Order 13175, entitled
Consultation and Coordination with Indian Tribal Governments (65 FR
67249, November 6, 2000) do not apply to this rule. In addition, This
rule does not impose any enforceable duty or contain any unfunded
mandate as described under Title II of the Unfunded Mandates Reform Act
of 1995 (UMRA) (Public Law 104-4).
This action does not involve any technical standards that would
require Agency consideration of voluntary consensus standards pursuant
to section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law 104-113, section 12(d) (15 U.S.C. 272
note).
VII. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report to each House of the Congress and to
the Comptroller General of the United States. EPA will submit a report
containing this rule and other required information to the U.S. Senate,
the U.S. House of Representatives, and the Comptroller General of the
United States prior to publication of this final rule in the Federal
Register. This final rule is not a ``major rule'' as defined by 5
U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection. Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: May 6, 2008.
Deborah McCall,
Acting Director, Registration Division, Office of Pesticide Programs.
0
Therefore, 40 CFR chapter I is amended as follows:
PART 180--[AMENDED]
0
1. The authority citation for part 180 continues to read as follows:
Authority: 21 U.S.C. 321(q), 346a and 371.
0
2. Section 180.485 is amended by revising paragraph (a) and removing
the text from paragraph (b) and reserving to read as follows:
Sec. 180.485 Cyproconazole; tolerances for residues.
(a) General. (1) Tolerances are established for the free and
conjugated residues of the fungicide cyproconazole, [alpha]-(4-
chlorophenyl)-[alpha]-(1-cyclopropylethyl)-1H-1,2,4-triazole-1-ethanol,
in or on the following food commodities:
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
Aspirated grain fractions............................ 2.5
Cattle, fat.......................................... 0.01
Cattle, meat byproducts (except liver)............... 0.01
Coffee bean, green (Imported)\1\..................... 0.1
Corn, field, forage.................................. 0.60
Corn, field, grain................................... 0.01
Corn, field, stover.................................. 1.2
Goat, fat............................................ 0.01
Goat, meat byproducts (except liver)................. 0.01
Horse, fat........................................... 0.01
Horse, meat byproducts (except liver)................ 0.01
Sheep, fat........................................... 0.01
Sheep, meat byproducts (except liver)................ 0.01
Soybean, forage...................................... 1.0
Soybean, hay......................................... 3.0
Soybean, oil......................................... 0.10
Soybean, seed........................................ 0.05
Wheat, forage........................................ 0.80
Wheat, grain......................................... 0.05
Wheat, grain, milled byproducts...................... 0.10
Wheat, hay........................................... 1.3
Wheat, straw......................................... 0.90
------------------------------------------------------------------------
\1\There are no U.S. registrations as of February 15, 2008 for use on
coffee bean.
(2) A tolerance is established for the combined free and conjugated
residues
[[Page 27761]]
of cyproconazole [alpha]-(4-chlorophenyl)-[alpha]-(1-cyclopropylethyl)-
1H-1,2,4-triazole-1-ethanol] and its metabolite [[delta]-(4-
chlorophenyl)-[beta],[delta]-dihydroxy-[gamma]-methyl-1H-1,2,4-
triazole-1-hexenoic acid in or on the following commodity:
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
Milk................................................. 0.02
------------------------------------------------------------------------
(3) Tolerances are established for the combined free and conjugated
residues of cyproconazole [alpha]-(4-chlorophenyl)-[alpha]-(1-
cyclopropylethyl)-1H-1,2,4-triazole-1-ethanol and its metabolite 2-(4-
chlorophenyl)-3-cyclopropyl-1-[1,2,4]triazol-1-yl-butane-2,3-diol in or
on the following commodities:
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
Cattle, liver........................................ 0.50
Goat, liver.......................................... 0.50
Hog, liver........................................... 0.01
Horse, liver......................................... 0.50
Sheep, liver......................................... 0.50
------------------------------------------------------------------------
(b) Section 18 emergency exemptions. [Reserved]
* * * * *
[FR Doc. E8-10829 Filed 5-13-08; 8:45 am]
BILLING CODE 6560-50-S